Sundhar et al. 2023 - Gulf of Mannar seaweed processing and metals
Sundhar et al. measured Be, Cr, Ni, As, Se, Cd, Hg, and Pb in three edible seaweeds from the Gulf of Mannar before and after household-style thermal processing. The paper reports total arsenic and total mercury only; it does not speciate inorganic arsenic, methylmercury, or Cr(VI). Values are reported as mg/kg; the source collected and processed fresh seaweed and does not report a dry-weight conversion.
Key numbers
Table 1 reports mean concentrations in raw, microwave-cooked (MWC), steam-cooked (SCT), and boiled seaweed in mg/kg:
| Species / treatment | Be | Cr | Ni | tAs | Se | Cd | tHg | Pb |
|---|---|---|---|---|---|---|---|---|
| U. lactuca raw | 0.017 | 1.425 | 2.423 | 5.486 | 0.448 | 0.379 | 0.024 | 1.887 |
| U. lactuca MWC | 0.007 | 6.133 | 8.847 | 3.294 | 0.795 | 0.562 | ND | 3.151 |
| U. lactuca SCT | 0.005 | 0.611 | 0.953 | 0.596 | 0.08 | 0.129 | ND | 0.078 |
| U. lactuca boiled | 0.007 | 0.367 | 0.851 | 0.441 | 0.082 | 0.077 | 0.001 | 1.101 |
| C. racemosa raw | 0.025 | 2.176 | 1.408 | 4.978 | 0.615 | 0.217 | 0.022 | 2.45 |
| C. racemosa MWC | 0.036 | 3.473 | 4.429 | 2.206 | 1.311 | 0.2 | ND | 3.43 |
| C. racemosa SCT | 0.017 | 1.648 | 1.034 | 0.792 | 0.553 | 0.079 | ND | 0.598 |
| C. racemosa boiled | 0.011 | 0.674 | 0.361 | 0.577 | 0.173 | 0.011 | 0.006 | 1.807 |
| K. aliverzii raw | 0.012 | 5.17 | 1.245 | 3.306 | 1.161 | 0.488 | 0.039 | 1.58 |
| K. aliverzii MWC | ND | 0.916 | 2.703 | 3.512 | 0.179 | 1.508 | ND | 1.564 |
| K. aliverzii SCT | ND | 0.036 | ND | 1.134 | 0.033 | 0.369 | ND | ND |
| K. aliverzii boiled | 0.001 | ND | ND | 1.103 | 0.024 | 0.354 | ND | 0.921 |
Table 1 raw-sample ranges were:
| Species | Lowest reported analyte/range | Highest reported analyte/range |
|---|---|---|
| U. lactuca | Be 0.003-0.058 mg/kg; tHg 0.004-0.074 mg/kg | tAs 1.495-9.671 mg/kg |
| C. racemosa | tHg 0.004-0.052 mg/kg; Cd 0.025-0.411 mg/kg | tAs 0.632-9.953 mg/kg |
| K. aliverzii | Be ND-0.074 mg/kg; tHg 0.001-0.149 mg/kg | Cr 1.408-14.056 mg/kg; tAs 1.252-6.86 mg/kg |
The paper separately reports mass-balanced processed concentrations and processing factors in Table 2. For total arsenic, those mass-balanced processed means were:
| Species | MWC tAs | SCT tAs | Boiled tAs |
|---|---|---|---|
| U. lactuca | 0.198 mg/kg | 0.166 mg/kg | 0.2 mg/kg |
| C. racemosa | 0.339 mg/kg | 0.682 mg/kg | 0.342 mg/kg |
| K. aliverzii | 0.61 mg/kg | 0.766 mg/kg | 0.72 mg/kg |
The same table reports processing-factor and reduction estimates across all eight analytes:
| Species | MWC reduction range | SCT reduction range | Boiled reduction range |
|---|---|---|---|
| U. lactuca | 74.2%-100.0% | 88.1%-100.0% | 73.6%-100.0% |
| C. racemosa | 51.7%-100.0% | 22.4%-100.0% | 56.2%-97.2% |
| K. aliverzii | 46.3%-100.0% | 49.0%-100.0% | 52.7%-100.0% |
Source-calculated total target hazard quotient (TTHQ) values were:
| Population scenario | U. lactuca raw / MWC / SCT / boiled | C. racemosa raw / MWC / SCT / boiled | K. aliverzii raw / MWC / SCT / boiled |
|---|---|---|---|
| Japan | 1.483 / 0.081 / 0.044 / 0.125 | 1.470 / 0.168 / 0.261 / 0.246 | 1.081 / 0.188 / 0.173 / 0.254 |
| Korea | 8.694 / 0.477 / 0.259 / 0.730 | 8.614 / 0.983 / 1.527 / 1.442 | 6.338 / 1.101 / 1.013 / 1.489 |
| China | 1.794 / 0.098 / 0.053 / 0.151 | 1.777 / 0.203 / 0.315 / 0.298 | 1.308 / 0.227 / 0.209 / 0.307 |
| Netherlands | 5.175 / 0.284 / 0.154 / 0.435 | 5.127 / 0.585 / 0.909 / 0.859 | 3.773 / 0.655 / 0.603 / 0.886 |
Table 4 also reports country-scenario lifetime cancer risk values for Cr, Ni, tAs, Cd, and Pb. Those values are retained here only as source-calculated exposure context; the routeable occurrence evidence is the concentration table above.
Methods (brief)
Fresh U. lactuca, C. racemosa, and K. aliverzii were hand-collected from the Gulf of Mannar and cleaned with tap and distilled water. Each species was split into four 1 kg lots: raw, boiled in a water bath at 102 +/- 2 deg C for 15 min, steam-cooked at the same temperature and time, and microwave-cooked for 10 min in a household microwave oven. Samples were homogenized, frozen at -20 deg C, digested from 100 +/- 2 mg material with 2 mL nitric acid and 1 mL hydrogen peroxide, diluted to 50 mL, and measured by ICP-MS. Calibration used multi-element standards from 0.1 to 25 ug/L; yttrium and iridium were internal standards. Reported recoveries were Be 92 +/- 4.7, Cr 97 +/- 3.2, Ni 88.9 +/- 16.3, As 96.1 +/- 7, Se 88.3 +/- 17.4, Cd 98.8 +/- 2.2, Hg 95.1 +/- 5.7, and Pb 100.2 +/- 3.5. The source reports LOD/LOQ values for As (0.11/0.22 mg/kg), Cd (0.02/0.04 mg/kg), Hg (0.08/0.16 mg/kg), and Pb (0.29/0.58 mg/kg).
Implications
This paper is routeable occurrence evidence for edible seaweed from India and processing-context evidence for boiled, steamed, and microwave-cooked seaweed matrices. The raw and processed concentration rows should stay separate because cooking changed the food mass and the paper reports both measured processed concentrations and mass-balanced processing-factor estimates. Total arsenic should not be treated as inorganic arsenic, total mercury should not be treated as methylmercury, and total chromium should not be treated as Cr(VI).
Wiki pages this source may touch
- seaweed-kelp-foods
- seaweed
- beryllium
- chromium
- nickel
- arsenic-total
- selenium
- cadmium
- mercury-total
- lead
Verification notes
- Identity checks before writing found no existing source page for DOI
10.1016/j.rsma.2023.102827, raw handleMFK_effect-of-thermal-processing-on-toxic-heavy-metals, or cite keysundhar2023-gulf-mannar-seaweed-metals. - All Key numbers were rechecked against
/tmp/hmi-seaweed-019.txt, extracted withpdftotext -layout. Table 1 and Table 2 were extractable; table values were copied without unit conversion. - Units are preserved as
mg/kg. The source does not explicitly label dry-weight or wet-weight basis in the table headers; because the sampling and processing sections describe fresh seaweed lots and no drying step before digestion, this page records the basis as fresh/as-processed seaweed and notes the missing explicit basis label rather than converting. - Speciation check: As is reported as
Asonly and is recorded as tAs; Hg is reported asHgonly and is recorded as tHg; Cr is reported as total Cr and is not treated as Cr(VI). - The Table 2 mass-balanced values and Table 1 processed concentrations are both retained because they answer different questions: concentration as measured in processed material versus mass-balanced retention/reduction.
- Brand firewall: the paper reports species, collection region, and laboratory processing methods; no consumer brands are attached to contamination values.
Page history
The five most recent substantive edits to this page. The full version history lives in git; when DOI minting comes online (see schema docs), each entry below will also link to a version-pinned DataCite DOI.
| Commit | Date | Description |
|---|---|---|
| 4039d20 | 2026-06-10 | scope: broaden ingest to the full upstream+downstream literature (marine, atmospheric, attribution, exposure, toxicology) — inclusion is the default |